- Research article
- Open Access
Chemo-sensors development based on low-dimensional codoped Mn2O3-ZnO nanoparticles using flat-silver electrodes
Chemistry Central Journal volume 7, Article number: 60 (2013)
Semiconductor doped nanostructure materials have attained considerable attention owing to their electronic, opto-electronic, para-magnetic, photo-catalysis, electro-chemical, mechanical behaviors and their potential applications in different research areas. Doped nanomaterials might be a promising owing to their high-specific surface-area, low-resistances, high-catalytic activity, attractive electro-chemical and optical properties. Nanomaterials are also scientifically significant transition metal-doped nanostructure materials owing to their extraordinary mechanical, optical, electrical, electronic, thermal, and magnetic characteristics. Recently, it has gained significant interest in manganese oxide doped-semiconductor materials in order to develop their physico-chemical behaviors and extend their efficient applications. It has not only investigated the basic of magnetism, but also has huge potential in scientific features such as magnetic materials, bio- & chemi-sensors, photo-catalysts, and absorbent nanomaterials.
The chemical sensor also displays the higher-sensitivity, reproducibility, long-term stability, and enhanced electrochemical responses. The calibration plot is linear (r2 = 0.977) over the 0.1 nM to 50.0 μM 4-nitrophenol concentration ranges. The sensitivity and detection limit is ~4.6667 μA cm-2 μM-1 and ~0.83 ± 0.2 nM (at a Signal-to-Noise-Ratio, SNR of 3) respectively. To best of our knowledge, this is the first report for detection of 4-nitrophenol chemical with doped Mn2O3-ZnO NPs using easy and reliable I-V technique in short response time.
As for the doped nanostructures, NPs are introduced a route to a new generation of toxic chemo-sensors, but a premeditate effort has to be applied for doped Mn2O3-ZnO NPs to be taken comprehensively for large-scale applications, and to achieve higher-potential density with accessible to individual chemo-sensors. In this report, it is also discussed the prospective utilization of Mn2O3-ZnO NPs on the basis of carcinogenic chemical sensing, which could also be applied for the detection of hazardous chemicals in ecological, environmental, and health care fields.
Semiconductor codoped nanomaterials have received significant interest due to their electronic, optoelectronic, magnetic, catalytical, electro-chemical, mechanical behaviors and their potential applications in different research areas. Semiconductor nanomaterials might be a promising due to their high-specific surface-area, low-resistances, high-catalytic activity, attractive electrochemical and optical properties [1, 2]. Nanomaterials are also scientifically important codoped nanostructure materials owing to their extraordinary mechanical, optical, electrical, electronic, thermal, and magnetic characteristics. Lately, it has attained significant attention in manganese doped-semiconductor materials in order to develop their physic-chemical behaviors and extend their efficient applications [3–5]. It has not only investigated the basic of magnetism, but also has huge potential in scientific features such as magnetic materials, bio & chemi-sensors, photo-catalysts, and absorbent nanomaterials [6–9]. Recently, very few articles are published based on transition-metal doped semiconductor nanomaterials synthesis and investigated the magnetic behaviors and potential applications only [10–13]. Here, it is prepared codoped Mn2O3-ZnO NPs by easy, facile, economical, non-toxic, repeatable, and reliable low-temperature wet-chemical technique. The nanostructure and morphology of the codoped Mn2O3-ZnO NPs were examined and potentially applied for the enhancement of higher-sensitive 4-nitrophenol chemo-sensor at room condition. Generally, chemo-sensing exploration have been developed with the transition-metal oxides nanostructures for the recognition and quantification of various toxic-chemicals such as phenyl-hydrazine, methanol, formaldehyde, ethanol, chloroform, dichloromethane etc., which are not ecologically safe and friendly [14–18]. The sensing mechanism with doped semiconductor metal oxides thin-film used primarily the properties of meso-porous thin-film generated by the physi-sorption and chemisorptions methods. The hazardous chemical detection is depended on the current responses of the fabricated thin-film, which cause by the presence of chemical components in the reaction-format in aqueous phase [19–21]. The key efforts are based on recongnition the least amount of 4-nitrophenol necessary for the fabricated Mn2O3-ZnO NPs chemo-sensors for electrochemical investigation.
Phenolic compounds have attained significant interest in last decade owing to their eco-toxic effects on human health, ecological, and environmental fields. These toxic compounds (i.e., 4-nitrophenol) are prepared using a number of polluting techniques, such as industry-related ways of plastic, pesticides, paint, drugs, composites, antioxidant, petroleum, and paper production . The 4-nitrophenol is recognized for its hazardous nature, carcinogenetic, toxicity, and persistence in the environment, which is become a common pollutant in nature and waste water . Because of its high solubility and stability in water, it has been also found in freshwater, sea environments and has been detected in industrial wastewaters and is difficult to degrade by conventional method. It is concerned in most of the degradation pathways of organo-phosphorous pesticides, which are decomposed in soil and water to form 4-nitrophenol as an intermediate or final-product in the reaction systems [24, 25]. Therefore, 4-nitrophenol is integrated in the Environmental Protection Agency List of Priority Pollutants (EPALPP) . Therefore, it is straight away desirable to fabricate a chemo-sensor for the detection of organic pollutants to accumulate the environment and human health. There is focused a significant attention for the development of simple, reliable, and ultra-sensitive in various detection methodology based on codoped nanomaterials. Generally, the detection of toxic 4-nitrophenol is consummated using chromatographic techniques, such as gas-chromatography [27, 28], high-performance liquid chromatography [29, 30], liquid chromatography connected with mass-spectroscopy , and capillary-electrophoresis . Electrochemical technique, which can offer fast, reliable, and direct real-time monitoring is one of the most utilized methods in the determination of nitro-phenolic stuffs. Electro-analytical techniques have been performed for 4-nitrophenol detection and quantification with a modified glassy carbon electrode [33, 34] hanging mercury drop electrode  and boron-doped diamond electrode . The analytical signal is derived from the four-electron reduction of the nitro-group  or by the direct two-electron oxidation of phenol to the corresponding o-benzoquinone [38–40]. Electrochemical chemo-sensors have attained huge interest in the recognition and quantification of environmental unsafe chemicals due to their reliable and fast response and determination [41–44]. Chemo-sensor technology plays a significant task in ecological protection that usually caused by environmental contamination and unintended seepage of harmful chemicals, which is a huge-menace for eco-systems. Thus for the attention of ecological and health monitoring, it is important to fabricate easy, simple, reproducible, reliable, and inexpensive chemo-sensors to detect toxic chemicals in aqueous systems. The sensitivity and low-detective of electrochemical chemo-sensor energetically dependent on the size, structure and properties of fabricated electrode doped nanomaterials. Hence doped nanostructure materials have received much attention and have widely been used as a redox mediator in chemo-sensors [45–48].
Codoped nanomaterial is largely established for the recognition of toxic chemicals in electro-chemical control method owing to their numerous benefits over conventional chemical methods in term of large-surface area for examining in medical, health-care and environmental fields [49–56]. In general electro-analytical technique, it was executed the slower responses, surface-fouling, noises, flexible-responses, and smaller dynamic-range and lower-sensitivity with bared codoped nanomaterials surfaces for chemical recognition. Therefore, the modification of the chemo-sensor surface with doped metal oxides nanostructure materials is urgently required to achieve higher sensitive, repeatability, and stable responses. Therefore, an easy and reliable I-V electrochemical approach is immediately needed for relatively simple, appropriate, and economical instrumentation which displays higher-sensitivity and lower-detection limits compared to general techniques. Here, a consistent, large-scale, and highly responsive I-V method is applied for detection of 4-nitrophenol chemical by codoped Mn2O3-ZnO NPs. The present approach represents a consistent, sensitive, low-sample volume, ease to handle, and specific electrochemical methods over the existing UV, CV, LC-MS, LSV, FL, and HPLC methods [57–60]. The simple coating technique for preparation of nanomaterials thin-film with conducting coating agents is developed for the fabrication of doped Mn2O3-ZnO NPs films. Here, low-dimensional doped Mn2O3-ZnO NPs films with conducting coating agents are synthesized and detected 4-nitrophenol in phosphate buffer solution (PBS) phase by reliable I-V method. To best of our knowledge, this is the first report for detection of 4-nitrophenol chemical with doped Mn2O3-ZnO NPs using easy and reliable I-V technique in short response time.
Materials and methods
Manganese chloride (MnCl2.4H2O), zinc chloride (ZnCl2), 4-nitrophenol, ammonium hydroxide (25%), Ethyl cellulose (EC), Disodium phosphate, Butyl carbitol acetate (BCA), Ethanol, Monosodium phosphate, and all chemicals utilized were of analytical grade and obtained from Sigma-Aldrich Company. Stock solution of 1.0 M 4-nitrophenol was synthesized in double distilled water. The doped Mn2O3-ZnO NPs was investigated with UV/visible spectroscopy (Lamda-950, Perkin Elmer, Germany). FT-IR spectra were recorded for Mn2O3-ZnO NPs with a spectrophotometer (Spectrum-100 FT-IR) in the mid-IR range, which was acquired from Perkin Elmer, Germany. Raman station 400 (Perkin Elmer, Germany) was exploited to investigate the Raman shift of Mn2O3-ZnO NPs using radiation source (Ar+ laser line, λ: ~513.4 nm). The XPS measurements were executed on a Thermo Scientific K-Alpha KA1066 spectrometer (Germany). Monochromatic AlKα x-ray radiation sources were used as excitation sources, where beam-spot size was kept in 300.0 μm. The spectrum was recorded in the fixed analyzer of transmission mode, where pass-energy was kept at 200.0 eV. The scanning of the spectra was performed at lower pressures (<10−8 Torr). The X-ray powder (XRD) diffraction prototypes were measured with X-ray diffractometer (XRD; X’Pert Explorer, PANalytical diffractometer) prepared with Cu-Kα1 radiation (λ = 1.5406 nm) by a generator voltage (~40.0 kV) and current (~35.0 mA) applied for the measurement. Morphology of codoped Mn2O3-ZnO NPs was evaluated on FE-SEM instrument (FESEM; JSM-7600 F, Japan). Elemental analysis (EDS) was investigated for doped Mn2O3-ZnO NPs using from JEOL, Japan. I-V technique was used for sensing NPs modified sensor electrode by Electrometer (Kethley, 6517A, Electrometer, USA) at room conditions.
Synthesis and growth mechanism of codoped Mn2O3-ZnO NPs
Initially manganese chloride (MnCl2.4H2O) and zinc chloride (ZnCl2) were gradually dissolved into the de-ionized water to prepare 0.1 M concentration separately at room temperature. After addition of NH4OH into the mixture of metal chloride solution, it was stirred slowly for several minutes at room condition. Mn2O3-ZnO NPs have been synthesized by adding equi-molar concentration of manganese chloride and zinc chloride as starting (reducing) materials into reaction-cell (in Teflon-line auto-clave) for 12 hours. Then the solution pH is attuned (at 10.5) by using prepared NH4OH and put into the auto-clave cell. The starting materials of MnCl2 and ZnCl2 were employed without further purification for co-precipitation method to codoped Mn2O3-ZnO nanoparticles composition. Again reducing agent (NH4OH) was added drop-wise into the vigorously stirred MnCl2 and ZnCl2 solutions mixture to produce a significant doped precipitate.
The growth mechanism of doped Mn2O3-ZnO NPs can be explained based on chemical reactions and nucleation, and growth of doped Mn2O3-ZnO crystals. The probable reaction mechanisms are anticipated for achieving the codoped Mn2O3-ZnO nanomaterials, which are appended in below.
The precursors of MnCl2 and ZnCl2 are soluble in alkaline medium (NH4OH reagent) according to the equation of (i) - (iii). After addition of NH4OH into the mixture of metal chlorides solution, it was strongly stirred for several minutes at room temperature. The reaction is development gradually according to the equation (iv). Then the resultant solution was washed systematically with ethanol, acetone and kept for drying at room temperature. During the total preparative procedure, NH4OH acts a pH buffer to control the pH value of the solution and slow donate of OH– ions. When the concentrations of the Mn2+, Zn2+, and OH- ions are reached above the critical value, the precipitation of doped Mn2O3-ZnO nuclei begin to start. As there is higher concentration of Zn2+ ion in the solution, the nucleation of doped Mn2O3-ZnO crystals become easier due to the lower-activation energy barrier of heterogeneous nucleation. However, as the concentration of Zn2+ subsistence, a number of larger doped Mn2O3-ZnO crystals with a spherical particle-shape morphology form in nano-level. The shape of codoped Mn2O3-ZnO NPs is approximately consistent with the growth pattern of codoped Mn2O3-ZnO crystals [61, 62]. Finally, the as-grown codoped Mn2O3-ZnO NPs products were calcined at 400.0°C for 4 hours in the furnace (Barnstead Thermolyne, 6000 Furnace, USA). The calcined doped nanomaterials were synthesized in detail in terms of their morphological, structural, optical properties, and applied for 4-nitrophenol chemical sensing.
Fabrication of AgE using doped Mn2O3-ZnO NPs
Phosphate buffer solution (PBS, 0.1 M, pH 7.0) is arranged by properly mixing Na2HPO4 (0.2 M) and NaH2PO4 (0.2 M) solution in 100.0 mL de-ionize water. Flat AgE is fabricated by doped Mn2O3-ZnO NPs with butyl carbitol acetate (BCA) and ethyl cellulose (EC) as conducting coating agents. Subsequently, the fabricated electrodes are transferred into the oven at 65.0°C for 12 hours until the film is totally dry, consistent, and stable. An electro-chemical cell is prepared with codoped Mn2O3-ZnO NPs coated silver electrode as a working electrode and palladium wire is employed as a counter electrodes. 4-nitrophenol (~1.0 M) is diluted at different concentration in DI water and used as a target chemical. Amount of 0.1 M PBS is kept constant in the small-beaker as 10.0 mL during the chemical analysis. Analyte solution is made with various concentration of 4-nitrophenol from 1.0 nM to 1.0 M. The sensitivity is calculated from the current-slope vs. analyte concentration from the calibration stature by considering the active surface area of doped Mn2O3-ZnO NPs fabricated chemo-sensors. Electrometer is properly utilized as a voltage sources for reliable I-V method in two electrodes assembly. With high-mechanical strength, good-conductivity, highly stability, large-surface area, and extremely miniaturized dimension of codoped Mn2O3-ZnO NPs have been extensively used in chemo-sensor modification and fabrication of 4-nitrophenol detection. The codoped Mn2O3-ZnO NPs were applied for the detection of 4-nitrophenol in liquid-phase system at room conditions. Initially, the NPs thin-film was prepared using conducting binders (EC and BCA) and embedded on the flat AgE electrode. The development and fabrication techniques are exhibited in the schematic diagram (Figure 1). The PdE and doped Mn2O3-ZnO NPs fabricated AgE is used as counter and working electrodes respectively, which is presented in Figure 1a-b. The 4-nitrophenol was employed as a target analytes in PBS buffer phase. The proposed electrical signals in presence of 4-nitrophenol chemical have been presented using I-V technique according to the Figure 1c. The physi-sorption etiquettes (absorption/adsorption) and detection method of doped Mn2O3-ZnO NPs are presented in the Figure 1d. Here the target analyte chemicals are adsorbed/absorbed onto the developed doped Mn2O3-ZnO NPs surfaces in huge amount owing to the meso-porous natures and large-active surface area of NPs in buffer phase respectively.
Results and discussions
The optical behavior of the codoped Mn2O3-ZnO NPs is one of the important features for the evaluation of its photo-catalytic property. The optical absorption spectra of NPs are investigated by UV-visible spectrophotometer in the visible range (200.0 to 800.0 nm). From the absorption spectra, it has been investigated the absorbance of the doped Mn2O3-ZnO NPs is about ~284.0 nm, which is presented in Figure 2a. Band gap energy (Ebg) is executed based on the most absorption band of NPs and originated to be ~4.50704 eV, according to following formula (v).
Where Ebg is the band-gap energy and λmax is the wavelength (~284.0 nm) of the doped Mn2O3-ZnO NPs. No extra peak related with contaminants and structural defects were found in the spectrums, which confirmed that the prepared NPs control crystallinity of codoped Mn2O3-ZnO NPs [63, 64].
The codoped Mn2O3-ZnO NPs are also investigated from the atomic and molecular vibrations. To investigate the vibration of materials, FT-IR spectrum mostly in the area of 450.0-4000.0 cm-1 is measured. Figure 2b displays the FT-IR spectrum of the Mn2O3-ZnO NPs. It represents band at 521.0, 1407.0, 1631.0, and 3427.0 cm-1. These executed wide vibration band (at 521.0 cm-1) could be assigned as metal-oxygen (Mn-O and Zn-O modes) stretching vibrations [65, 66], which verified the pattern of doped Mn2O3-ZnO NPs. The additional experimental vibration bands may be allocated to O-H stretching (3427 cm−1), C-O stretching vibration (1631.0 cm−1), and O-H bending vibration (1407 cm−1). The absorption bands at 1407, 1631 and 3427 cm-1 usually displays from water and carbon dioxide, which generally semiconductor nanostructure materials absorbed from the surroundings owing to their meso-porous nature. Finally, the resultant vibration bands at lower-frequencies areas recommended the formation of codoped Mn2O3-ZnO NPs.
Raman spectroscopy is a spectroscopic method employs to reveal vibrational, rotational and other low-frequency phases in Raman active compounds. Figure 2c confirms the Raman spectrum, where key features of the wave number are accomplished at about ~368.0 cm-1 and 667 cm-1 for metal-oxygen (Mn-O and Zn-O) stretching vibrations. These bands can be allocated to a codoped Mn2O3-ZnO NPs .
Crystallinity and crystal phases of the doped Mn2O3-ZnO NPs were investigated. X-ray diffraction outlines of codoped NPs are presented in Figure 3a. The Mn2O3-ZnO NPs samples were examined and exposed as conventional tetragonal structure. The as-grown doped Mn2O3-ZnO NPs was calcined at 400.0°C in muffle-furnace to start the formation of nano-crystalline phases. Figure 3a shows distinctive crystallinity of the doped Mn2O3-ZnO NPs and their aggregative crystal arrangement. The reflection peaks in this proto-type were instigated to correspond with Mn2O3-ZnO NPs phase having tetragonal geometry [JCPDS # 01-024-1133]. The phases employed the key characteristic peaks with indices for calcined crystalline NPs at 2θ values of (112), (200), (103), (211), (004), (220), (204), (105), (312), (321), (224), and (400) degrees. The tetragonal lattice space group is l41/amd. Finally, the powder X-ray prototype is corresponded to doped Mn2O3-ZnO NPs, which may be featured to the lattice site of NPs semiconductor nanomaterials [68–70]. Further, no other impurity peak was found in the XRD prototype screening the codoped Mn2O3-ZnO NPs phase formation.
The electron dispersive spectroscopy (EDS) evaluation of calcined Mn2O3-ZnO NPs assigns the existence of Mn, Zn, and O composition in the pure calcined Mn2O3-ZnO materials. It is clearly employed that NP materials controlled with only manganese, zinc, and oxygen elements, which is shown in Figure 3b. The composition of Mn, Zn, and O is 33.07%, 18.81%, and 48.12% respectively. No other peak related with any impurity has been found in the EDS, which demonstrates that the doped Mn2O3-ZnO NPs are composed only with Mn, Zn, and O. High resolution FESEM images of calcined Mn2O3-ZnO NPs are exhibited in Figure 3c-d. The FESEM images displayed of codoped materials with aggregated nano-particles shapes. The average diameter of doped Mn2O3-ZnO NPs is calculated in the range of 22.7 nm to 50.0 nm, which is close to ~37.5 nm. It is displayed noticeably from the FESEM images that the simple wet-chemical method of prepared crystalline nanomaterials are nanostructure of codoped Mn2O3-ZnO NPs, which executed in aggregated shape, higher-density, and attained nanostructure in spherical nano-particle shapes. It is also suggested that nanomaterials composed in spherical particle-like morphology of the combined codoped Mn2O3-ZnO NPs [71, 72].
X-ray photoelectron spectroscopy (XPS) is a quantitative spectroscopic method that determines the elemental-composition, empirical-formula, chemical-state and electronic-state of the elements that present in nanomaterials. Here, XPS measurements were employed for doped Mn2O3-ZnO NPs to examine the chemical states of Zn, Mn, and O atoms. The full XPS spectra of Zn2p, Mn3s, Mn2p, and O1s are displayed in Figure 4a. The O1s spectrum employs a major-peak at 532.9 eV in Figure 4b. The peak at 532.9 eV is assigned to lattice oxygen, may be shown to oxygen (i.e, O2-) in presence in the doped Mn2O3-ZnO NP nanomaterials . In Figure 3c, the peaks of the Mn3s binding energy for all the samples displayed at around 77.3 eV and 91.8 eV respectively, which is in excellent conformity with the reference data for Mn . Figure 4d also shows the XPS spectra (spin-orbit doublet peaks) of the Mn2p(3/2) and Mn3p(1/2) regions found with semiconductor doped Mn2O3-ZnO NPs. The binding energy of the Mn3p(3/2) and Mn3p(1/2) peak at 644.7 eV and 655.3 eV respectively indicates the existence of Mn since their bindings energies are similar . In Figure 4e, the spin-orbit peaks of the Zn2p(1/2) and Zn2p(3/2) binding energy for codoped Mn2O3-ZnO NPs appeared at around 1025.7 eV and 1048.9 eV respectively, which is in good conformity with the reference data for Zn .
Applications: detection of 4-nitrophenol using codoped Mn2O3-ZnO NPs
Figure 5a exhibits the current responses un-coated (gray-dotted) and coated (dark-dotted) AgE working electrode with doped Mn2O3-ZnO NPs at room conditions. With doped NPs fabricating surface, the current-signal is reduced compared to without fabricated surface, which reveals the surface is slightly inhibited with doped NPs. The current changes for the codoped Mn2O3-ZnO NPs modified flat-electrodes before (dark-dotted) and after (blue-dotted) injection of 50.0 μL 4-nitrophenol (~1.0 nM) in 10.0 mL PBS (0.1 M) solution, which is presented in Figure 5b. These considerable changes of surface current are measured in every injection of the target 4-nitrophenol into the electrochemical solution by Keithley electrometer. 10.0 mL of 0.1 M PBS solution is initially transferred into the electrochemical-cell and added the low to high concentration of 4-nitrophenol drop-wise from the stock chemical solution. I-V responses with Mn2O3-ZnO NPs modified electrode surface were evaluated from the various concentrations (1.0 nM to 1.0 M), which was revealed in Figure 5c. It displays the current changes of developed films as a function of 4-nitrophenol concentration at room conditions. It was also observed that with increasing the concentration of analyte, the resultant currents also enhanced considerably, which corroborated that the response was a surface-process. It shows the response of codoped Mn2O3-ZnO NPs as a role of analyte concentration at room conditions. A large concentration range of 4-nitrophenol concentration was selected to study the probable investigative parameters, which was calculated in 1.0 nM to 1.0 M. The calibration curve was drawn from the variation of 4-nitrophenol concentrations, which was presented in Figure 5d. It was exhibited a calibration curve for the response current versus 4-nitrophenol concentration of developed doped Mn2O3-ZnO NPs on AgE electrode. It was measured from the calibration plot that as the concentration of target analyte enhances, the current response also increased and finally at high 4-nitrophenol concentration, the current achieves at a saturated level, which proposes that the active surface sites of doped NPs saturated with analyte units . The sensitivity is manipulated from the calibration-curve, which is close to ~4.6667 μA cm-2 μM-1. The linear dynamic range of this chemo-sensor exhibits from 0.1 nM to 50.0 μM (linearity, r2 = 0.977) and the detection limit was calculated as ~ 0.83 ± 0.2 nM (at an SNR of 3).
Usually, the resistance value of the codoped Mn2O3-ZnO NPs modified electrodes/chemo-sensors are decreased with enhancing active-surface area, owing to the essential characteristics of the semiconductor materials [78–80]. In fact, oxygen adsorption (O2) displays a considerable liability in the electrical features of the doped NPs (n-type semiconductor) structures. Oxygen ion (O2-) adsorption eradicates the conduction electrons and enhances the resistance of doped Mn2O3-ZnO NPs. Active oxygen species (i.e., O2− and O−) are adsorbed onto material surfaces at room condition, and the quantity of such chemo-sorbed oxygen species strongly depend on the structural properties. At room condition, O2− is chemo-sorbed, while in NPs morphology, both O2− and O− are chemo-sorbed, and the O2− vanishes rapidly [81, 82]. Here, 4-nitrophenol sensing mechanism of doped Mn2O3-ZnO NPs chemo-sensor is based on the semiconductors metal oxides, which is held owing to the oxidation/reduction of the semiconductor NPs. According to the dissolved O2 in bulk-solution or surface-air of the neighboring atmosphere, the following reactions (vi) & (vii) are accomplished in the reaction medium.
These reactions are consummated in bulk-system/air-liquid interface/neighboring atmosphere owing to the small carrier concentration, which increased the resistance. The 4-nitrophenol sensitivity towards doped Mn2O3-ZnO NPs could be ascribed to the higher-oxygen lacking conducts to enhance the oxygen adsorption. Larger the amount of oxygen adsorbed on the doped NPs-sensor surface, higher would be the oxidizing potentiality and faster would be the oxidation of 4-nitrophenol. The activity of 4-nitrophenol would have been extremely big as contrast to other toxic chemical with the surface under indistinguishable conditions [83–85]. When 4-nitrophenol reacts with the adsorbed oxygen (by producing electrons) on the chemo-sensor surface, it oxidized to 4-hydroxylaminophenol and water. Later, the oxidation of 4-hydroxylaminophenol takes place to convert to 4-nitrosophenol and the subsequent reversible reduction, which released free electrons (2e-) into the conduction-band (C.B.). This phenomenon could be elucidated through the following proposed reactions (viii-x).
These reactions related to oxidation of the reducing carriers in presence of semiconductor doped Mn2O3-ZnO NPs. These techniques improved the carrier concentration and hence reduced the resistance on exposure to reducing liquids/analytes. At the room condition, the incorporating of metal oxide surface to reduce liquid/analytes results in a surface interceded adsorption process. The abolition of iono-sorbed O2 enhances the electron communication and hence the surface conductance of the thin-film [86, 87]. The reducing analyte offers electrons co-doped Mn2O3-ZnO NP surfaces. Accordingly, the resistance is slightly reduced, where conductance is amplified. For this reason, why the analyte response (current) intensified with increasing resultant potential. Thus, the electrons are contributed for quick enhance in conductance of the thin-film. The codoped Mn2O3-ZnO NPs unusual regions dispersed on the surface would improve the ability of nanomaterial to absorb more O2 species giving higher resistances in air ambient, which is presented in Figure 6.
The response time was approximately 10.0 s for the doped Mn2O3-ZnO NPs coated-electrode to attain saturated-steady state current. The outstanding sensitivity of NPs chemo-sensor can be accredited to good absorption (porous-surfaces coated with conducting binders) and adsorption ability (large-surface area), higher-catalytic activity, and good bio-compatibility of the codoped Mn2O3-ZnO NPs . Due to large surface area, NPs are proposed a favorable nano-environment for the 4-nitrophenol exposure and gratitude with exceptional sensitivity. The sensitivity of codoped Mn2O3-ZnO NPs affords high-electron communication characteristics, which improved the direct electron communication between the active sites of NPs and chemo-sensor electrode surfaces [89, 90]. The modified thin NPs fabricated-film had a better consistency and reliability. However, owing to large-dynamic surface area, the codoped Mn2O3-ZnO NPs were entailed productive surroundings for the 4-nitrophenol chemical detection (by adsorption) with huge-amount [91, 92]. To check the repeatability and storage stabilities, I-V response for codoped Mn2O3-ZnO NPs coated chemo-sensor was investigated (up to two weeks). After every experiment, the fabricated chemo-sensor was washed carefully with the PBS buffer solution and executed no considerable reduced on the current responses (recovery, ~95.2%). The sensitivity was retained almost same of initial sensitivity up to week, after that the response of the developed doped Mn2O3-ZnO NPs sensor gradually decreased. In Table 1, it is contrasted the performances for 4-nitrophenol recognition based doped Mn2O3-ZnO NPs using various modified electrode materials.
By reliable I-V techniques for fabricating, assembling and integrating structural semiconductor doped Mn2O3-ZnO NPs onto conductive flat-silver electrodes has been investigated in details for the detection of toxic 4-nitrophenol compound. Codoped Mn2O3-ZnO NPs fabricated sensor executed the potential applications in providing 4-nitrophenol chemo-sensors and encouraging improvement has been consummated in this investigation. Besides the development of codoped nanomaterials, there are still a number of significant subjects that are required for additional examination before this nanomaterial can be moved into the profitable uses for the mentioned applications. As for the doped nanostructures, NPs are introduced a route to a new generation of toxic chemo-sensors, but a premeditate effort has to be applied for doped Mn2O3-ZnO NPs to be taken comprehensively for large-scale applications, and to achieve higher-potential density with accessible to individual chemo-sensors.
Na CW, Park SY, Chung JH, Lee JH: Transformation of ZnO nanobelts into single-crystalline Mn3O4 nanowires. ACS Appl Mater Interfac. 2012, 4: 6565-6572. 10.1021/am301670x.
InglerJr WB, Baltrus JP, Khan SUM: Photoresponse of p-type zinc-doped iron(III) oxide thin films. J Am Chem Soc. 2004, 126: 10238-10239. 10.1021/ja048461y.
Wang J, Chong PF, Ng SC, Gan LM: Microemulsion processing of manganese zinc ferrites. Mater Lett. 1997, 30: 217-221. 10.1016/S0167-577X(96)00200-5.
Toberer ES, Löfvander JP, Seshadri R: Topo-chemical formation of mesoporous MnO crystals. Chem Mater. 2006, 18: 1047-1052. 10.1021/cm052255n.
Toberer ES, Schladt TD, Seshadri R: Macroporous manganese oxides with regenerative mesopores. J Am Chem Soc. 2006, 128: 1462-1463. 10.1021/ja0579412.
Deng H, Li X, Peng Q, Wang X, Chen J, Li Y: Monodisperse magnetic single-crystal ferrite microspheres. Angewandte Chemie (Inter Ed). 2005, 44: 2782-2785. 10.1002/anie.200462551.
Patrice R, Dupont L, Aldon L, Jumas JC, Wang E, Tarascon JM: Structural and electrochemical properties of newly synthesized Fe-substituted MnO2 samples. Chem Mater. 2004, 16: 2772-2782. 10.1021/cm0401239.
Li H, Li J, Xu Q, Yang Z, Hu X: A derivative photoelectrochemical sensing platform for 4-nitrophenolate contained organophosphates pesticide based on carboxylated perylene sensitized nano-TiO2. Anal Chim Acta. In press, http://dx.doi.org/10.1016/j.aca.2012.12.038.
Rahman MM, Khan SB, Marwani HM, Asiri AM: Selective iron(III) ion uptake using CuO-TiO2 nanostructure by inductively coupled plasma-optical emission spectrometry. Chem Centr J. 2012, 6: 158-10.1186/1752-153X-6-158.
Sampieri Á, Lima E: On the acid–base properties of microwave irradiated hydrotalcite-like compounds containing Zn2+ and Mn2+. Langmuir. 2009, 25: 3634-3639. 10.1021/la803920c.
Mugumaoderha MC, Sporken R, Ghijsen J, DeGroot FMF, Dumont JA: Phase transitions at the Mn/ZnO (0001¯) interface probed by high energy X-ray spectroscopies. J Phys Chem C. 2012, 116: 665-670. 10.1021/jp206705p.
Torres F, Amigó R, Asenjo J, Krotenko E, Tejada J, Brillas E: Electrochemical route for the synthesis of New nanostructured magnetic mixed oxides of Mn, Zn, and Fe from an acidic chloride and nitrate medium. Chem Mater. 2000, 12: 3060-3067. 10.1021/cm001043h.
Feng D, Luo W, Zhang J, Xu M, Zhang R, Wu H, Lv Y, Asiri AM, Khan SB, Rahman MM, Zheng G, Zhao D: Multi-layered mesoporous TiO2 thin films with large pore and highly crystalline frameworks for efficient photoelectrochemical conversion. J Mater Chem A. 2013, 1: 1591-1599. 10.1039/c2ta00588c.
Rahman MM, Jamal A, Khan SB, Faisal M: Characterization and applications of as-grown β-Fe2O3 nanoparticles prepared by hydrothermal method. J Nanopart Res. 2011, 13: 3789-3799. 10.1007/s11051-011-0301-7.
Wu KL, Wei XW, Zhou XM, Wu DH, Liu XW, Ye Y, Wang Q: NiCo2 Alloys: controllable synthesis, magnetic properties, and catalytic applications in reduction of 4-nitrophenol. J Phys Chem C. 2011, 115: 16268-16274. 10.1021/jp201660w.
Rahman MM, Khan SB, Faisal M, Asiri AM, Alamry KA: Highly sensitive formaldehyde chemical sensor based on hydrothermally prepared spinel ZnFe2O4 nanorods. Sens Actuator B Chem. 2012, 171–172: 932-937.
Rahman MM: Fabrication of mediator-free glutamate sensors based on glutamate oxidase using smart micro-devices. J Biomed Nanotech. 2011, 7: 351-357. 10.1166/jbn.2011.1299.
Rahman MM, Jamal A, Khan SB, Faisal M: Fabrication of chloroform sensors based on hydrothermally prepared low-dimensional β-Fe2O3 nanoparticles. Superlatt Microstruc. 2011, 50: 369-376. 10.1016/j.spmi.2011.07.016.
Gomes JDA, Sousa MH, Tourinho FA, Aquino R, Silva GJD, Depeyrot J, Dubois E, Perzynski R: Synthesis of core-shell ferrite nanoparticles for ferrofluids: chemical and magnetic analysis. J Phys Chem C. 2008, 112: 6220-6227. 10.1021/jp7097608.
Rahman MM, Khan SB, Faisal M, Asiri AM, Tariq MA: Detection of aprepitant drug based on Low-dimensional Un-doped iron oxide nanoparticles prepared by solution method. Electrochim Acta. 2012, 75: 164-170.
Rahman MM, Khan SB, Marwani HM, Asiri AM, Alamry KA, Al-Youbi AO: Selective determination of gold (III) ion using CuO microsheets as a solid phase adsorbent prior to ICP-OES measurements. Talanta. 2013, 104: 75-82.
Frenzel W, Frenzel JO, Moeler J: Spectrophotmetric determination of phenolic compounds by flow-injection analysis. Anal Chim Acta. 2006, 261: 253-
Penalver A, Pocurull E, Borrull F, Marce RM: Separation and determination of nitrobenzenes by micellar electrokinetic chromatography and high-performance liquid chromatography. J Chromatogr A. 2002, 953: 79-10.1016/S0021-9673(02)00113-9.
Castillo M, Domingues R, Alpendurada MF, Barcelo D: Persistence of selected pesticides and their phenolic transformation products in natural waters using off-line liquid solid extraction followed by liquid chromatographic techniques. Anal Chim Acta. 1997, 353: 133-10.1016/S0003-2670(97)00353-X.
Dzyadevych SV, Chovelon JM: A comparative photodegradation studies of methyl parathion by using Lumistox test and conductometric biosensor technique. Mater Sci Eng C. 2002, 21: 55-10.1016/S0928-4931(02)00058-9.
ATSDR: Toxicity FAQs nitrophenols; Agency for Toxic Substances and Disease Registry. 2001
Wang SP, Chen HJ: Separation and determination of nitrobenzenes by micellar electrokinetic chromatography and high-performance liquid chromatography. J Chromatogr A. 2002, 979: 439-10.1016/S0021-9673(02)01435-8.
Kontsas H, Rosenberg C, Pfaeffli P, Jappinen P: Gas chromatographic–mass spectrometric determination of chlorophenols in the urine of sawmill workers with past use of chlorophenol-containing anti-stain agents. Analyst. 1995, 120: 1745-1749. 10.1039/an9952001745.
Brega A, Prandini P, Amaglio C, Pafuni E: Determination of phenol, m-, o- and p-cresol, p-aminophenol and p-nitrophenol in urine by high-performance liquid chromatography. J Chromatogr A. 1990, 535: 311-316.
Makuch B, Gazda K: Occurrence and determination of organic pollutants in tap and surface waters of the Gdańsk district. J Chromatogr A. 1996, 733: 171-10.1016/0021-9673(95)00905-1.
Wissiack R, Rosenberg E: Universal screening method for the determination of US Environmental Protection Agency phenols at the lower ng l−1 level in water samples by on-line solid-phase extraction–high-performance liquid chromatography–atmospheric pressure chemical ionization mass spectrometry within a single run. J Chromatogr A. 2002, 963: 149-10.1016/S0021-9673(02)00546-0.
Kaniansky D, Krcmova E, Madajova V, Masar M, Marek J: Determination of nitrophenols by capillary zone electrophoresis in a hydrodynamically closed separation compartment. J Chromatogr A. 1997, 772: 327-10.1016/S0021-9673(97)00102-7.
Luz RDS, Damos FS, DeOliveira AB, Beek J: Voltammetric determination of 4-nitrophenol at a lithium tetracyanoethylenide (LiTCNE) modified glassy carbon electrode. Talanta. 2004, 64: 935-10.1016/j.talanta.2004.04.010.
Hu SS, Xu CL, Wang GP, Cui DF: Voltammetric determination of 4-nitrophenol at a sodium montmorillonite-anthraquinone chemically modified glassy carbon electrode. Talanta. 2001, 54: 115-10.1016/S0039-9140(00)00658-5.
Barek J, Ebertova H, Mejstrik V, Zima J: Determination of 2-Nitrophenol, 4-Nitrophenol, 2-Methoxy-5-nitrophenol, and 2,4-Dinitrophenol by Differential Pulse Voltammetry and Adsorptive Stripping Voltammetry. Collect Czech Chem C. 1994, 59: 1761-10.1135/cccc19941761.
Ni Y, Wang L, Kokot S: Simultaneous determination of nitrobenzene and nitro-substituted phenols by differential pulse voltammetry and chemometrics. Anal Chim Acta. 2001, 431: 101-10.1016/S0003-2670(00)01319-2.
Lawrence NS, Pagels M, Meredith A, Jones TGJ, Hall CE, Pickles CSJ, Godfried HP: Electroanalytical applications of boron-doped diamond microelectrode arrays. Talanta. 2006, 69: 829-10.1016/j.talanta.2005.11.020.
Liu Y, Deng Y, Sun Z, Wei J, Zheng G, Asiri AM, Khan SB, Rahman MM, Zhao D: Hierarchical Cu2S Microsponges Constructed from Nanosheets for Efficient Photocatalysis. Small. http://dx.doi.org/10.1002/smll.201300197.
Pedrosa VA, Codognoto L, Machado SAS, Avaca LA: Is the boron-doped diamond electrode a suitable substitute for mercury in pesticide analyses? A comparative study of 4-nitrophenol quantification in pure and natural waters. J Electroanal Chem. 2004, 573: 11-18.
Garbellini GS, Salazar-Banda GR, Avaca LA: Sonovoltammetric determination of 4-nitrophenol on diamond electrodes. J. Braz. Chem. Soc. 2007, 18: 1095-1099. 10.1590/S0103-50532007000600002.
Rahman MM, Gruner G, Al-Ghamdi MS, Daous MA, Khan SB, Asiri AM: Fabrication of highly sensitive phenyl hydrazine chemical sensor based on as-grown ZnO-Fe2O3 Microwires. Inter. J. Electrochem. Sci. 2013, 8: 520-534.
Organic electrochemistry: an introduction and a guide. Edited by: Lund H, Baizer MM. 1991, New York: Marcel Dekker, 411-
Khan SB, Akhtar K, Rahman MM, Asiri AM, Seo J, Alamry KA, Han H: Thermally and mechanically stable green environmental composite for chemical sensor applications. New Journal of Chemistry. 2012, 36: 2368-2375. 10.1039/c2nj40549k.
Khan SB, Rahman MM, Jang ES, Akhtar K, Han H: Special susceptive aqueous ammonia chemi-sensor: Extended applications of novel UV-curable polyurethane-clay nanohybrid. Talanta. 2011, 84: 1005-1010. 10.1016/j.talanta.2011.02.036.
Khan SB, Faisal M, Rahman MM, Jamal A: Exploration of CeO2 nanoparticles as a chemi-sensor and photo-catalyst for environmental applications. Sci Tot Environ. 2011, 409: 2987-2992. 10.1016/j.scitotenv.2011.04.019.
Cordero-Rando MD, Barea-Zamora M, Barber-Salvador JM, Naranjo-Salvador I: Electrochemical study of 4-nitrophenol at a modified carbon paste electrode. Microchim Acta. 1999, 132: 7-11. 10.1007/PL00010076.
Khan SB, Faisal M, Rahman MM, Jamal A: Low-temperature growth of ZnO nanoparticles: photocatalyst and acetone sensors. Talanta. 2011, 85: 943-949. 10.1016/j.talanta.2011.05.003.
Rahman MM, Umar A, Sawada K: Development of amperometric glucose biosensor based on glucose oxidase enzyme immobilized with multi-walled carbon nanotubes at Low potential. Sens Actuator B Chem. 2009, 137: 327-333. 10.1016/j.snb.2008.10.060.
Rahman MM, Jamal A, Khan SB, Faisal M, Asiri AM: Highly sensitive methanol chemical sensor based on undoped silver oxide nanoparticles prepared by a solution method. Microchim Acta. 2012, 178: 99-106. 10.1007/s00604-012-0817-2.
Rahman MM, Jamal A, Khan SB, Faisal M, Asiri AM: Fabrication of methanol chemical sensor based on hydrothermally prepared α-Fe2O3 codoped SnO2 nanocubes. Talanta. 2012, 95: 18-24.
Rahman MM, Jamal A, Khan SB, Faisal M, Asiri AM: Fabrication of highly sensitive acetone sensor based on sonochemically prepared as-grown Ag2O nanostructures. Chem Engineer J. 2012, 192: 122-128.
Rahman MM, Jamal A, Khan SB, Faisal M: Cu-doped ZnO based nanostructured materials for sensitive chemical sensor applications. ACS App Mater Inter. 2011, 3: 1346-1351. 10.1021/am200151f.
Sadik OA, Zhou AL, Kikandi S, Du N, Wang Q, Varner K: Sensors as tools for quantitation, nanotoxicity and nanomonitoring assessment of engineered nanomaterials. J Environ Monit. 2009, 11: 1782-1800. 10.1039/b912860c.
Su S, Wu W, Gao J, Lu J, Fan C: Nanomaterials-based sensors for applications in environmental monitoring. J Mater Chem. 2012, 22: 18101-18110. 10.1039/c2jm33284a.
Rahman MM, Jamal A, Khan SB, Faisal M: Fabrication of highly sensitive ethanol chemical sensor based on Sm-doped Co3O4 nano-kernel by solution method. J Phys Chem C. 2011, 115: 9503-9510. 10.1021/jp202252j.
Rahman MM, Jamal A, Khan SB, Faisal M: Highly sensitive ethanol chemical sensor based on Ni-doped SnO2 nanostructure materials. Biosens Bioelectron. 2011, 28: 127-134. 10.1016/j.bios.2011.07.024.
Zhang L, Wang JQ, Li J, Zhang S, Jiang Z, Zhou J, Cheng J, Hu T, Yan W, Wei X, Wu Z: Regulation of magnetic behavior and electronic configuration in Mn-doped ZnO nanorods through surface modifications. Chem Mater. 2012, 24: 1676-1681. 10.1021/cm203661c.
Swierczewska M, Liu G, Lee S, Chen X: High-sensitivity nanosensors for biomarker detection. Chem Soc Rev. 2012, 41: 2641-2655. 10.1039/c1cs15238f.
Lord H, Kelley SO: Nanomaterials for ultrasensitive electrochemical nucleic acids biosensing. J Mater Chem. 2009, 19: 3127-3134. 10.1039/b814569e.
Zhou L, Wu HB, Zhu T, Lou XW: Facile preparation of ZnMn2O4 hollow microspheres as high-capacity anodes for lithium-ion batteries. J Mater Chem. 2012, 22: 827-829. 10.1039/c1jm15054e.
Courtel FM, Abu-Lebdeh Y, Davidson IJ: ZnMn2O4 nanoparticles synthesized by a hydrothermal method as an anode material for Li-ion batteries. Electrochim Acta. 2012, 71: 123-127.
Zhao J, Wang F, Su P, Li M, Chen J, Yang Q, Li C: Spinel ZnMn2O4 nanoplate assemblies fabricated via “escape-by-crafty-scheme” strategy. J Mater Chem. 2012, 22: 13328-13333. 10.1039/c2jm32261g.
Bessekhouad Y, Robert D, Weber JV: Photocatalytic activity of Cu2O/TiO2, Bi2O3/TiO2 and ZnMn2O4/TiO2 heterojunctions. Catal Today. 2005, 101: 315-321. 10.1016/j.cattod.2005.03.038.
Yang Y, Zhao Y, Xiao L, Zhang L: Nanocrystalline ZnMn2O4 as a novel lithium-storage material. Electrochem Commun. 2008, 10: 1117-1120. 10.1016/j.elecom.2008.05.026.
Duan J, Wang H, Wang H, Zhang J, Wu S, Wang Y: Mn-doped ZnO nanotubes: from facile solution synthesis to room temperature ferromagnetism. CrystEngComm. 2012, 14: 1330-1336. 10.1039/c1ce06221b.
Wang L, Liu B, Ran S, Wang L, Gao L, Qu F, Chen D, Shen G: Facile synthesis and electrochemical properties of CoMn2O4 anodes for high capacity lithium-ion batteries. J Mater Chem A. 2013, http://dx.doi.org/10.1039/C2TA00125J.
Li H, Song B, Wang WJ, Chen XL: Facile synthesis, thermal, magnetic, Raman characterizations of spinel structure ZnMn2O4. Mater Chem Phys. 2011, 130: 39-44. 10.1016/j.matchemphys.2011.04.072.
Kim SW, Lee HW, Muralidharan P, Seo DH, Yoon WS, Kim DK, Kang K: Electrochemical performance and ex situ analysis of ZnMn2O4 nanowires as anode materials for lithium rechargeable batteries. Nano Res. 2011, 4: 505-510. 10.1007/s12274-011-0106-0.
Zhang G, Yu L, Wu HB, Hoster HE, Lou XW: Formation of ZnMn 2 O 4 ball-in-ball hollow microspheres as a high-performance anode for lithium-Ion batteries. Adv Mater. 2012, 24: 4609-4613. 10.1002/adma.201201779.
Xiao L, Yang Y, Yin J, Li Q, Zhang L: Low temperature synthesis of flower-like ZnMn2O4 superstructures with enhanced electrochemical lithium storage. J Pow Sour. 2009, 194: 1089-1093. 10.1016/j.jpowsour.2009.06.043.
Deng Y, Tang S, Zhang Q, Shi Z, Zhang L, Zhan S, Chen G: Controllable synthesis of spinel nano-ZnMn2O4via a single source precursor route and its high capacity retention as anode material forlithium ion batteries. J Mater Chem. 2011, 21: 11987-11995. 10.1039/c1jm11575h.
Menaka SL, Samal KV, Ramanujachary SE, Lofland G, Ganguli AK: Stabilization of Mn(IV) in nanostructured zinc manganese oxide and their facile transformation from nanospheres to nanorods. J Mater Chem. 2011, 21: 8566-8573. 10.1039/c1jm10425j.
Rahman MM, Khan SB, Faisal M, Rub MA, Al-Youbi AO, Asiri AM: Electrochemical determination of olmesartan medoxomil using hydrothermally prepared nanoparticles composed SnO2–Co3O4 nanocubes in tablet dosage forms. Talanta. 2012, 99: 924-931.
Zhang P, Li X, Zhao Q, Liu S: Synthesis and optical property of one dimensional spinel ZnMn2O4 nanorods. Nanoscal Res Lett. 2011, 6: 323-10.1186/1556-276X-6-323.
Zhao L, Li X, Zhao J: Fabrication, characterization and photocatalytic activity of cubic-like ZnMn2O4. App Surf Sci. http://dx.doi.org/10.1016/j.apsusc.2012.12.078.
Lupan O, Emelchenko GA, Ursaki VV, Chai G, Redkin AN, Gruzintsev AN, Tiginyanu IM, Chow L, Ono LK, Cuenya BR, Heinrich H, Yakimov EE: Synthesis and characterization of ZnO nanowires for nanosensor applications. Mater Res Bull. 2010, 45: 1026-1032. 10.1016/j.materresbull.2010.03.027.
Marcelo G, Muñoz-Bonilla A, Fernández-García M: Magnetite-polypeptide hybrid materials decorated with gold nanoparticles: study of their catalytic activity in 4-nitrophenol reduction. J Phys Chem C. 2012, 116: 24717-24725. 10.1021/jp309145r.
Song P, Qin HW, Zhang L, An K, Lin ZJ, Hu JF, Jiang MH: The structure, electrical and ethanol-sensing properties of La1−xPbxFeO3 perovskite ceramics with x ≤ 0.3. Sens Actuator B Chem. 2005, 104: 312-317. 10.1016/j.snb.2004.05.023.
Lee SR, Rahman MM, Ishida M, Sawada K: Fabrication of a highly sensitive penicillin sensor based on charge transfer techniques. Biosens Bioelectron. 2009, 24: 1877-1882. 10.1016/j.bios.2008.09.008.
Lee SR, Rahman MM, Ishida M, Sawada K: Development of highly sensitive acetylcholine sensor based on acetylcholine by charge transfer techniques esterase using smart biochips. Trends Anal Chem. 2009, 28: 196-203. 10.1016/j.trac.2008.11.009.
Han N, Chai L, Wang Q, Tian Y, Deng P, Chen Y: Evaluating the doping effect of Fe, Ti and Sn on gas sensing property of ZnO. Sens Actuator B Chem. 2010, 147: 525-530. 10.1016/j.snb.2010.03.082.
Hsueh TJ, Hsu CL, Chang SJ, Chen IC: Laterally grown ZnO nanowire ethanol gas sensors. Sens Actuator B Chem. 2007, 126: 473-477. 10.1016/j.snb.2007.03.034.
Tao B, Zhang J, Hui S, Wan L: An amperometric ethanol sensor based on a Pd-Ni/SiNWs electrode. Sens Actuator B Chem. 2009, 142: 298-302. 10.1016/j.snb.2009.08.004.
Wongrat E, Pimpang P, Choopun S: An amperometric ethanol sensor based on a Pd-Ni/SiNWs electrode. App Surf Sci. 2009, 256: 968-972. 10.1016/j.apsusc.2009.02.046.
Umar A, Rahman MM, Kim SH, Hahn YB: Zinc oxide nanonail based chemical sensor for hydrazine detection. Chem Commun. 2008, 166-169.
Mujumdar S: Synthesis and characterization of SnO2 films obtained by a wet chemical process. Mat Sci Poland. 2009, 27: 123-128.
Pan B, Du W, Zhang W, Zhang X, Zhang Q, Pan B, Lv L, Zhang Q, Chen J: Improved Adsorption of 4-Nitrophenol onto a Novel Hyper-Cross-Linked Polymer. Environ Sci Technol. 2007, 41: 5057-5062. 10.1021/es070134d.
Wunder S, Polzer F, Lu Y, Mei Y, Ballauff M: Kinetic analysis of catalytic reduction of 4-nitrophenol by metallic nanoparticles immobilized in spherical polyelectrolyte brushes. J Phys Chem C. 2010, 114: 8814-8820. 10.1021/jp101125j.
Hayakawa K, Yoshimura T, Esumi K: Preparation of gold − dendrimer nanocomposites by laser irradiation and their catalytic reduction of 4-nitrophenol. Langmuir. 2003, 19: 5517-5521. 10.1021/la034339l.
Zhang J, Chen G, Chaker M, Rosei F, Ma D: Gold nanoparticle decorated ceria nanotubes with significantly high catalytic activity for the reduction of nitrophenol and mechanism study. App Catal B Environ. 2013, 132–133: 107-115.
Gangula A, Podila R, Ramakrishna M, Karanam L, Janardhana C, Rao AM: Catalytic reduction of 4-nitrophenol using biogenic gold and silver nanoparticles derived from breynia rhamnoides. Langmuir. 2011, 27: 15268-15274. 10.1021/la2034559.
Ahmaruzzaman M, Gayatri SL: Activated neem leaf: a novel adsorbent for the removal of phenol, 4-nitrophenol, and 4-chlorophenol from aqueous solutions. J Chem Eng Data. 2011, 56: 3004-3016. 10.1021/je100937r.
Khan SB, Rahman MM, Akhtar K, Asiri AM, Alamry KA, Seo J, Han H: Copper oxide based polymer nanohybrid for chemical sensor applications. Int J Electrochem Sci. 2012, 7: 10965-10975.
Liu XY: A novel sensor based on electropolymerization poly(safranine) film electrode for voltammetric determination of 4-nitrophenol. Bull Korean Chem Soc. 2010, 31: 1182-1186. 10.5012/bkcs.2010.31.5.1182.
Liu J, Chen H, Lin Z, Lin JM: Preparation of surface imprinting polymer capped Mn-doped ZnS quantum dots and their application for chemiluminescence detection of 4-nitrophenol in Tap water. Anal Chem. 2010, 82: 7380-7386. 10.1021/ac101510b.
Nistor C, Oubiña A, Marco MP, Barceló D, Emnéus J: Competitive flow immunoassay with fluorescence detection for determination of 4-nitrophenol. Anal Chim Acta. 2001, 426: 185-195. 10.1016/S0003-2670(00)00825-4.
Li J, Kuang D, Feng Y, Zhang F, Xu Z, Liu M: A graphene oxide-based electrochemical sensor for sensitive determination of 4-nitrophenol. J Hazard Mater. 2012, 201–202: 250-259.
Pedrosa VA, Codognoto L, Avaca LA: Electroanalytical determination of 4-nitrophenol by square wave voltammetry on diamond electrodes. J Braz Chem Soc. 2003, 14: 530-535. 10.1590/S0103-50532003000400007.
This paper was funded by King Abdulaziz University, under grant No. (31-3-1432/HiCi). The authors, therefore, acknowledge technical and financial support of KAU.
The authors declare that they have no competing interests.
MMR made a significant contribution to preparation and characterization of doped nanomaterials, and data collection and their analysis and application as well as writing the manuscript. GG has revised the manuscript for intellectual content and corrected accordingly. SAG made a significant contribution to survey the literatures and results. MAD revised the manuscript properly and surveyed the results. SBK participated in the synthesis of samples, collected the data, and contributed in the experimental work. AMA has revised the manuscript for intellectual content. All authors read and approved the final manuscript.
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Rahman, M.M., Gruner, G., Al-Ghamdi, M.S. et al. Chemo-sensors development based on low-dimensional codoped Mn2O3-ZnO nanoparticles using flat-silver electrodes. Chemistry Central Journal 7, 60 (2013) doi:10.1186/1752-153X-7-60
- Doped Mn2O3-ZnO nanoparticles
- Wet-chemical method
- Powder X-ray diffraction
- I-V technique
- X-ray photoelectron spectroscopy